CN110217875A - Utilize stratiform MoS2Activate the method and application of persulfate removal butyl p-hydroxybenzoate - Google Patents

Utilize stratiform MoS2Activate the method and application of persulfate removal butyl p-hydroxybenzoate Download PDF

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Publication number
CN110217875A
CN110217875A CN201910385097.5A CN201910385097A CN110217875A CN 110217875 A CN110217875 A CN 110217875A CN 201910385097 A CN201910385097 A CN 201910385097A CN 110217875 A CN110217875 A CN 110217875A
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China
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bhb
mos
removal
persulfate
pms
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CN201910385097.5A
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杨佳诚
付明来
祝敏平
苑宝玲
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Institute of Urban Environment of CAS
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Institute of Urban Environment of CAS
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Priority to CN201910385097.5A priority Critical patent/CN110217875A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

Stratiform MoS is utilized the present invention relates to a kind of2Direct activation potassium hydrogen persulfate (PMS) and sodium persulfate (PDS) removal butyl p-hydroxybenzoate (BHB) method, specifically include: configuration pH be 3~10, the BHB target solution that concentration is 5 mg/L;Change experiment condition, a certain amount of business MoS is separately added into BHB target liquid2And PMS/PDS, it is placed under stirring condition and reacts.Present invention firstly discovers that: under the conditions of no external energy, stratiform MoS2Can direct activation persulfate generate living radical (SO simultaneously4 •‒OH and O2 •‒) and non-free radical (1O2) synergistic oxidation removal BHB.Process of the present invention process flow is simple, easily operated, not high to equipment requirement, stratiform MoS2Material is cheap and easy to get, has a vast market application potential in terms of emerging pollutant in processing water environment.

Description

Utilize stratiform MoS2Activate persulfate removal butyl p-hydroxybenzoate method and Using
Technical field
The invention belongs to two-dimensional layer chalcogenide materials and technical field of water pollution control, it is related to a kind of utilizing stratiform MoS2Activate the method and application of persulfate removal butyl p-hydroxybenzoate.
Background technique
Currently, parabens (PBs) have caused as emerging environmental contaminants, domestic and international researcher's is wide General concern.About 8000 tons of PBs are consumed in the whole world every year, and most PBs is introduced into production, use and treatment process In environment;Report points out that PBs is detected extensively in wastewater treatment plant effluent, surface water and deposit, it is therefore necessary to be ground Study carefully the technology of removal PBs.Jing Zhang etc. (Environ. Sci. Technol. 47,2013:13011) uses Ru/ CeO2It is catalyzed KMnO4Butyl p-hydroxybenzoate (BHB) in degradation water, experiment confirm Ru/CeO2The KMnO of catalysis4With efficient The ability of degradation BHB.
Using metal oxide as activator or catalyst peroxynitrite decomposition hydrogen (H2O2) and persulfate (PS) formation activity is certainly It is the hot subject of field of environment engineering by base degradation Organic substance in water.And using transient metal sulfide (TMDs) as activator Or catalyst inducement generates the innovation and application that the pollutant in living radical degradation environment is then two-dimensional layer Material Field.Such as Magnetic iron ore (FeS) can activate in PS inactivation waterE. coli2017 112:236 of K-12(Water Research), and two sulphur Change molybdenum (MoS2) then it is used to the Bi that building has n-p hetero-junctions2O3/Bi2S3/MoS2Composite catalyst is to enhance photochemical catalytic oxidation The performance (2017 200:47 of Applied Catalysis B:Environmental) of organic pollutants.MoS2Belong to In hexagonal crystal system, have with layer structure as graphite-phase, interlayer is weaker Van der Waals force, be then in layer it is stronger covalently Key, layer are easily peeled off with layer, therefore have good anisotropy and lower coefficient of friction.Sulphur atom has metal very strong Adhesion strength makes MoS2Metal surface can be adhered well to and play lubricating function, MoS always2It is a kind of the inorganic of function admirable Lubricant.In addition, stratiform MoS2It is also had been a great concern in the application of energy field.
Literature search the result shows that: under the conditions of no external energy, utilize stratiform MoS2The removal of direct activation persulfate The method and its application of BHB have not been reported.Present invention firstly discovers that MoS2Can direct activation PMS/PDS generate simultaneously it is active freely Base (SO4 •‒OH and O2 •‒) and non-free radical (1O2) synergistic oxidation removal BHB.
Summary of the invention
Primary and foremost purpose of the present invention is to provide a kind of utilization stratiform MoS2The method of direct activation persulfate.
Another object of the present invention is to provide the utilization stratiform MoS2Activate the living radical (SO that PMS/PDS is generated4 •‒ OH and O2 •‒) and non-free radical (1O2) synergistic oxidation removal BHB application.
The purpose of the present invention is realized by following technology path: a kind of to utilize stratiform MoS2Persulfate removal is activated to hydroxyl The method of yl benzoic acid butyl ester, comprising the following steps: (1) configure pH be 3~10, the BHB target solution that concentration is 5 mg/L; (2) change experiment condition, a certain amount of business MoS is separately added into BHB target liquid2And PMS/PDS, stirring.
The persulfate is PMS and PDS, and PDS is provided by Sinopharm Chemical Reagent Co., Ltd., specification are as follows: 500 G is bottled, purity > 98%;PMS is provided by Aladdin reagent Co., Ltd, specification are as follows: 500 g are bottled, and PMS chemical formula is KHSO5•0.5KHSO4•0.5K2SO4, KHSO5Content >=47%.
The BHB pH value of solution is preferably that 3~10, PMS and SPS concentration are both preferably 2.5~7.5 mM.
The reaction condition is preferably that 15~40 DEG C of 300 rpm stirs 120~180 min.
It is described to utilize stratiform MoS2The method of activation persulfate removal butyl p-hydroxybenzoate is applied to go water removal dirty Contaminate the mg/L of low concentration BHB(≤5 in environment).
The present invention has the following advantages and effect.
(1) present invention firstly discovers that in no external energy, MoS2Can direct activation PMS and PDS generate activity from By base (SO4 •‒OH and O2 •‒) and non-free radical (1O2) efficiently remove BHB.
(2) MoS used in the present invention2, PMS and PDS it is cheap and easy to get, BHB removal reaction at normal temperatures and pressures can be into Row, it is not high to equipment requirement, belong to Novel low-consumption water treatment technology.
(3) stratiform MoS used in the present invention2, PMS and PDS it is easily stored and transport, can be widely used for environmental pollution by water It administers, there is biggish application prospect.
Detailed description of the invention
Fig. 1 is stratiform MoS2Activation PMS and PDS removes BPB curve synoptic diagram in water removal, and (illustration is stratiform MoS2Morphology characterization Figure).
Fig. 2 is different quenchers to MoS2Activation PMS removes BHB effect tendency figure in water removal.
Fig. 3 is different quenchers to MoS2Activation PDS removes BHB effect tendency figure in water removal.
Specific embodiment
Present invention be described in more detail below by way of embodiments and drawings, and (scope of the present invention is not limited in described Hold).
Embodiment 1
(1) stratiform MoS2Activation PMS and PDS goes BHB efficiency in water removal: compound concentration is the BHB aqueous solution of 5 mg/L, by its pH It is adjusted to ~ 7.00.80 mL BHB aqueous solutions are measured respectively, and MoS is added after clean reaction flask, number2(1 g/L), PMS(5 MM) or PDS(5 mM), be placed in (25 ± 2 DEG C) of room temperature stirrings (300 rpm) and react 180 min, separated in time takes 2mL water Sample is analyzed.
(3) the data obtained is depicted as curve graph, as shown in Figure 1: MoS2/ PMS and MoS2/ PDS system is equal in 180 min Interior energy complete oxidation removes BHB;In addition, as seen from the figure, the MoS within entire reaction time2, PMS or PDS to the absorption of BHB or The main reason for oxidation process is not its removal, the removal of BHB is mainly by stratiform MoS2It activates PMS and PDS and generates active oxygen Species (see embodiment 2) Lai Shixian's.
Embodiment 2
(1) different quenchers are investigated to stratiform MoS2Activation PMS and PDS removes the influence of BHB efficiency and active specy point in water removal Analysis: compound concentration is the BHB aqueous solution of 5 mg/L, its pH is adjusted to ~ 7.00.80 mL BHB aqueous solutions are measured respectively in cleaning MoS is added after number in reaction flask2(1 g/L), PMS(5 mM) or PDS(5 mM);Quencher, experiment sample difference is not added in control sample 0.5 M ethyl alcohol, the 0.5 M tert-butyl alcohol, 1 mM histidine or 1 mM 1,4-benzoquinone is added, is placed on (25 ± 2 DEG C) of room temperature stirrings (300 Rpm 180 min) are reacted, separated in time takes 2mL water sample to be analyzed.
(2) the data obtained is depicted as curve graph, as shown in Figure 2: 0.5 M ethyl alcohol and the 0.5 M tert-butyl alcohol are for MoS2/ PMS system removal BHB shows inhibiting effect, and the inhibition of 0.5 M ethyl alcohol is eager to excel than the 0.5 M tert-butyl alcohol, illustrates MoS2/ There are SO for PMS system4 •‒WithOH, and SO4 •‒BHB oxidation contribution is greater thanOH;1 mM histidine and 1 mM 1,4-benzoquinone for MoS2/ PMS system removal BHB shows inhibiting effect, illustrates MoS2There is also O for/PMS system2 •‒With1O2;It is analyzed by Fig. 3 Know, 0.5 M ethyl alcohol, the 0.5 M tert-butyl alcohol, 1 mM histidine and 1 mM 1,4-benzoquinone are to MoS2/ PDS system removal BHB is shown Strong inhibiting effect, illustrates MoS2/ PDS system also exists simultaneously SO4 •‒OH、O2 •‒With1O2Oxidation removal BHB.
Embodiment 3
(1) different initial pH, PMS/PDS dosages of solution and temperature are investigated to stratiform MoS2Activation PMS and PDS is gone in water removal The influence of BHB efficiency: compound concentration is the BHB aqueous solution of 5 mg/L, its pH is adjusted to 3 ~ 10.80 mL BHB are measured respectively MoS is added after clean reaction flask, number in aqueous solution2(1 g/L), the mM of PMS(2.5 ~ 7.5) or PDS(2.5 ~ 7.5 MM), it is placed on (15 ~ 40 DEG C) of room temperature stirrings (300 rpm) and reacts 180 min, separated in time takes 2mL water sample to carry out Analysis.Analysis data are known: being in 3 ~ 10 ranges in pH, after reacting 180 min, 80% or more BHB can be by MoS2/ PMS and MoS2/ PDS system oxidation removal;When pH ≈ 7, PMS and PDS dosage is when 2.5 ~ 7.5 mM change, BHB after 180 min Oxidation removal rate can reach 98% or more;Increase solution temperature and is conducive to MoS2/ PMS and MoS2/ PDS system is quickly gone in water removal BHB。

Claims (7)

1. a kind of utilize stratiform MoS2The method for activating persulfate removal butyl p-hydroxybenzoate, it is characterised in that this method The following steps are included: configuration pH is 3~10, the BHB target solution that concentration is 5 mg/L;Change experiment condition, to BHB target liquid In be separately added into a certain amount of business MoS2And PMS/PDS, stirring.
2. utilizing stratiform MoS according to claim 12The method for activating persulfate removal butyl p-hydroxybenzoate, it is special Sign is: under the conditions of being not necessarily to external energy, stratiform MoS2It can direct activation persulfate generation living radical (SO4 •‒OH And O2 •‒) and non-free radical (1O2) synergistic oxidation removal BHB.
3. utilizing stratiform MoS according to claim 12The method for activating persulfate removal butyl p-hydroxybenzoate, it is special Sign is: layered MoS2It being provided by Sinopharm Chemical Reagent Co., Ltd., specification are as follows: 100 g are bottled, purity > 98%。
4. utilizing stratiform MoS according to claim 12The method for activating persulfate removal butyl p-hydroxybenzoate, it is special Sign is: the persulfate is potassium hydrogen persulfate (PMS) and sodium persulfate (PDS), and PDS is had by Chinese medicines group chemical reagent Limit company provides, specification are as follows: 500 g are bottled, purity > 98%;PMS is provided by Aladdin reagent Co., Ltd, specification are as follows: 500 g are bottled, and PMS chemical formula is KHSO5•0.5KHSO4•0.5K2SO4, KHSO5Content >=47%.
5. utilizing stratiform MoS according to claim 12The method for activating persulfate removal butyl p-hydroxybenzoate, it is special Sign is: the MoS2Dosage is 1 g/L, and oxidant PMS/SPS concentration is 2.5~7.5 mM.
6. utilizing stratiform MoS according to claim 12The method for activating persulfate removal butyl p-hydroxybenzoate, it is special Sign is: the reaction condition is that 15 ~ 40 DEG C of 300 rpm stirs 5~180 min.
7. utilizing stratiform MoS according to claim 12Activate the method application of persulfate removal butyl p-hydroxybenzoate The mg/L of low concentration BHB(≤5 in removal environmental pollution by water).
CN201910385097.5A 2019-05-09 2019-05-09 Utilize stratiform MoS2Activate the method and application of persulfate removal butyl p-hydroxybenzoate Pending CN110217875A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110624569A (en) * 2019-09-14 2019-12-31 北京建筑大学 MoS doped with metal ions2Method for degrading PPCPs by activating monopersulfate
CN111362391A (en) * 2020-02-25 2020-07-03 暨南大学 Novel method for removing organic pollutants through piezoelectric effect activation Fenton-like reaction
CN113135594A (en) * 2020-01-19 2021-07-20 广东工业大学 Persulfate activation method and application thereof
CN115215421A (en) * 2022-08-16 2022-10-21 南华大学 Application of vanadium tetrasulfide in degradation of organic pollutants

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105819562A (en) * 2016-04-21 2016-08-03 中国科学院城市环境研究所 Method for efficiently removing butyl 4-hydroxybenzoate by using MWCNTs-persulfate system high-efficiency and application of method
CN109019969A (en) * 2018-08-22 2018-12-18 华东理工大学 A kind of method of sulfide activation potassium hydrogen persulfate degradation of organic waste water
CN109553181A (en) * 2018-12-11 2019-04-02 中国科学院生态环境研究中心 A kind of method generated free radicals using trivalent molybdenum and its method for handling organic wastewater

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105819562A (en) * 2016-04-21 2016-08-03 中国科学院城市环境研究所 Method for efficiently removing butyl 4-hydroxybenzoate by using MWCNTs-persulfate system high-efficiency and application of method
CN109019969A (en) * 2018-08-22 2018-12-18 华东理工大学 A kind of method of sulfide activation potassium hydrogen persulfate degradation of organic waste water
CN109553181A (en) * 2018-12-11 2019-04-02 中国科学院生态环境研究中心 A kind of method generated free radicals using trivalent molybdenum and its method for handling organic wastewater

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110624569A (en) * 2019-09-14 2019-12-31 北京建筑大学 MoS doped with metal ions2Method for degrading PPCPs by activating monopersulfate
CN113135594A (en) * 2020-01-19 2021-07-20 广东工业大学 Persulfate activation method and application thereof
CN113135594B (en) * 2020-01-19 2023-07-25 广东工业大学 Activation method of persulfate and application thereof
CN111362391A (en) * 2020-02-25 2020-07-03 暨南大学 Novel method for removing organic pollutants through piezoelectric effect activation Fenton-like reaction
CN115215421A (en) * 2022-08-16 2022-10-21 南华大学 Application of vanadium tetrasulfide in degradation of organic pollutants
CN115215421B (en) * 2022-08-16 2023-08-25 南华大学 Application of vanadium tetrasulfide in degrading organic pollutants

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Application publication date: 20190910